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Plastics contaminants from

Sorted plastic packaging materials are shipped, usually in bales, to processing plants to be converted to polymer resins. The bales are broken and the bottles sorted to ensure that only one type of polymer is further processed. Processing consists of chopping and grinding the bottles into flakes. These flakes are washed. Processing steps such as flotation are used to remove polymeric contaminants from the flakes (15,16). The flakes are melted and converted into pellets. [Pg.230]

Susceptibility of Metals to Attack by Contaminants from Plastics... [Pg.955]

Fig. 8-28). The screen pack is a filter that restricts unmelted plastic and/or contaminants from entering the die (6). [Pg.474]

Surface-water samples are usually collected manually in precleaned polyethylene bottles (from a rubber or plastic boat) from the sea, lakes, and rivers. Sample collection is performed in the front of the bow of boats, against the wind. In the sea, or in larger inland lakes, sufficient distance (about 500 m) in an appropriate wind direction has to be kept between the boat and the research vessel to avoid contamination. The collection of surface water samples from the vessel itself is impossible, considering the heavy metal contamination plume surrounding each ship. Surface water samples are usually taken at 0.3-1 m depth, in order to be representive and to avoid interference by the air/water interfacial layer in which organics and consequently bound heavy metals accumulate. Usually, sample volumes between 0.5 and 21 are collected. Substantially larger volumes could not be handled in a sufficiently contamination-free manner in subsequent sample pretreatment steps. [Pg.21]

Figure 11.4 Total ion current (TIC) chromatogram of lipid residue extracted from a potsherd of Early Neolithic date (Ecsegfalva, Hungary). Cx y F refer to fatty acids with carbon number (x) and number of unsaturations (y). Cx T refer to triacylglycerols with number of carbon atoms (x). P = plasticizer contamination. (Craig et al., 2007, 354 Figure 18.1, by permission.)... Figure 11.4 Total ion current (TIC) chromatogram of lipid residue extracted from a potsherd of Early Neolithic date (Ecsegfalva, Hungary). Cx y F refer to fatty acids with carbon number (x) and number of unsaturations (y). Cx T refer to triacylglycerols with number of carbon atoms (x). P = plasticizer contamination. (Craig et al., 2007, 354 Figure 18.1, by permission.)...
Another problem in the packaging of oral liquids is lack of cleanliness of the containers before filling. Fibers and even insects often appear as debris in containers, particularly in the plastic containers used for many of these products. Many manufacturers receive containers shrink-wrapped in plastic to minimize contamination from fiberboard cartons, and many manufacturers use compressed air to clean the containers. Vapors, such as oil vapors, from the compressed air have occasionally been found to present problems, and it is a good practice to use compressed gas from oil-free compressors. [Pg.6]

Polymer additives, which are used in high quantities in a plastic material, can contain residues of contaminants from production. Kaiser, Lorenz and Bahadir (1992) found low contents of PAHs within plastic additives. Both classes of compounds can be found in dust that accumulates in personal computers. Ren, Cheng and Chen (2006) showed that heated plastic parts are not the only source for PAH because the concentrations of PAH in dust are higher in offices were cigarettes are smoked. Anyhow, the study alleged a significantly higher PAH exposure of workers if a PC is present in the room. [Pg.420]

Photooxidation Diffusion Chemical changes due to photochemical reactions Introduction of contaminants from man-made materials, such as solvents from polyvinyl chloride (PVC) materials and PVC cement, plasticizers, and phthalates from polyethylene and polypropylene materials Protection from exposure to light, use of amber glass bottles Use of inert materials (PTFE, fiberglass-reinforced epoxy materials) steam-cleaning of groundwater well components prior to installation... [Pg.137]

We use wipe sampling to detect contaminants on non-porous surfaces, such as the surfaces of plastic or metal drums transformer casings various heavy equipment walls floors ceilings laboratory benches. Sampling with wipes allows transferring contaminants from a surface area of a known size onto the wipe material. The wipes are then analyzed, and the amounts of contaminants found on the wipe are related to the surface area. [Pg.158]

The surface of the sample container may interact with the analyte. The surfaces can provide catalysts (e.g., metals) for reactions or just sites for irreversible adsorption. For example, metals can adsorb irreversibly on glass surfaces, so plastic containers are chosen for holding water samples to be analyzed for their metal content. These samples are also acidified with HNO3 to help keep the metal ions in solution. Organic molecules may also interact with polymeric container materials. Plasticizers such as phthalate esters can diffuse from the plastic into the sample, and the plastic can serve as a sorbent (or a membrane) for the organic molecules. Consequently, glass containers are suitable for organic analytes. Bottle caps should have Teflon liners to preclude contamination from the plastic caps. [Pg.19]


See other pages where Plastics contaminants from is mentioned: [Pg.2065]    [Pg.2065]    [Pg.143]    [Pg.8]    [Pg.267]    [Pg.910]    [Pg.255]    [Pg.75]    [Pg.98]    [Pg.346]    [Pg.1134]    [Pg.26]    [Pg.234]    [Pg.478]    [Pg.571]    [Pg.346]    [Pg.1134]    [Pg.8]    [Pg.141]    [Pg.486]    [Pg.179]    [Pg.379]    [Pg.363]    [Pg.363]    [Pg.315]    [Pg.402]    [Pg.444]    [Pg.113]    [Pg.349]    [Pg.72]    [Pg.255]    [Pg.360]    [Pg.4]    [Pg.125]   
See also in sourсe #XX -- [ Pg.18 , Pg.95 ]

See also in sourсe #XX -- [ Pg.18 , Pg.95 ]




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